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EC number: 231-892-1 | CAS number: 7775-27-1
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2001
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 001
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: The study was conducted in compliance with the U.S. Environmental Protection Agency (EPA) and Organization for Economic Cooperation and development (OECD) Good Laboratory Practices (U.S. EPA, 1989; OECD, 1992).
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Test material form:
- solid: crystalline
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River laboratories Inc.; Portage, MI
- Age at study initiation: 39 days
- Weight at study initiation: no information available
- Fasting period before study: no information available
- Housing: individually in suspended, stainless steel wire-mesh cages
- Diet: certified Rodent Lab Die (PMI Nutrition International, Inc.; ad libitum
- Water: tap water ad libitum
- Acclimation period: 13 days
ENVIRONMENTAL CONDITIONS
- Temperature: 20 - 24 °C
- Humidity: 40 - 60 % R.H.
- Air changes: no information available
- Photoperiod: 12 hrs dark/12 hrs light
Administration / exposure
- Route of administration:
- inhalation: dust
- Type of inhalation exposure:
- whole body
- Vehicle:
- air
- Remarks on MMAD:
- MMAD / GSD: Average mass median aerodynamic diameters (MMAD) and geometric standard deviation (GSD) for the exposure levels:
5 mg/m³: 2.5 ± 1.85 µm;
10 mg/m³: 2.7 ± 1.83 µm;
25 mg/m³: 2.5 ± 1.80 µm. - Details on inhalation exposure:
- Animals were exposed simultaneously in four 2.0 m³ stainless steel and glass whole-body inhalation exposure chambers (Hazelton 2000 type). One chamber was dedicated for each group for the duration of the study. Twenty animals per sex per exposure group were individually caged in two cage batteries that were rotated daily through various cage positions in the chamber.
- Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Actual exposure concentrations were measured using standard gravimetric methods. Four samples per day were collected from each exposure group during the first month of exposure and two samples per day thereafter. Samples were collected on 25-mm glass-fibre filters (type A/E, Gelman Sciences, Ann Arbor, MI) held in open-face filter holders. Aerosol particle size was determined once for each exposure group during each week. The results were expressed in terms of the mass median aerodynamic diameter (MMAD) and the geometric standard deviation.
- Duration of treatment / exposure:
- Diammonium persulfate was administered 6 h/day, 5 days/week, for 13 consecutive weeks
- Frequency of treatment:
- 6 h/day
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/m³ air (analytical)
- Dose / conc.:
- 5 mg/m³ air (analytical)
- Dose / conc.:
- 10.3 mg/m³ air (analytical)
- Dose / conc.:
- 25 mg/m³ air (analytical)
- No. of animals per sex per dose:
- 20 animals per sex per exposure group.
- Control animals:
- yes, concurrent no treatment
- Details on study design:
- - Animals were exposed simultaneously in four 2.0 m³ stainless steel and glass whole-body inhalation exposure chambers (Hazelton 2000 type). One chamber was dedicated for each group for the duration of the study. Twenty animals per sex per exposure group were individually caged in two cage batteries that were rotated daily through various cage positions in the chamber. Ammonium persulfate was administered 6 h/day, 5 days/week, for 13 consecutive weeks to target exposure levels of 5, 10, and 25 mg/m³. The exposure levels were based on a no-effect level of 10 mg/m³ from a 4-week range finding study using 3.3, 10.3 and 32.5 mg/m³ of diammonium persulfate.
- An identical group of animals was exposed to clean filtered air and served as control group. - Positive control:
- Not indicated.
Examinations
- Observations and examinations performed and frequency:
- Animals were observed twice daily for viability. Individual physical observations were conducted weekly, beginning 1 wk prior to initiation of exposure. In addition, animals were observed within the chamber at the midpoint of each exposure and again when the animals were removed from the chamber. During the recovery period, clinical examinations were performed once daily.
- Sacrifice and pathology:
- After completion of 13 weeks of exposure, 10 animals per sex per group were randomly selected, euthanized and necropsiesd. Of the remaining animals, 5 animals per sex per dose group were maintained from either 4- or 13-week postexposure recovery periods and then euthanized and necropsised.
- Statistics:
- All analyses were conducted using two-tailed tests for minimum significance levels of 1 % and 5 %, comparing the treatment groups to the control group by sex. All statistics were performed by a Digital MicroVAX 3400 computer. Body weight, body weight change, food consumption clinical pathology and absolute and relative organ weight data were subjected to a one-way variance (ANOVA) followed by Dunnett's test (Dunnett, 1964) when appropriate.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, non-treatment-related
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- effects observed, treatment-related
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Details on results:
- There were no exposure-related deaths during the study. Increased respiration rates were noted in both males and females in the 25 mg/m³ group, and in a few animals in the 10.3 mg/m³ group. The incidence of these clinical signs decreased to zero during the first weeks of the recovery period. Body weights for both males and females in the 25 mg/m³ group were significantly depressed during most of the exposure period compared to the control group. By the end of the recovery period, body weights for the exposed animals were similar to the control group values. Lung weights were elevated in the 25 mg/m³ group after 13 wk of exposure, but were similar to controls at 6 wk postexposure. Irritation of the trachea and bronchi/bronchioles was noted microscopically after 13 weeks of exposure to 25 mg/m³. These lesions had recovered by 6 wk postexposure.
Based on these results, the no-observed-adverse-effect level (NOAEC) was 10.3 mg/m³, while the no-observed-effect level (NOEC) for exposure of rats to a dust aerosol of ammonium persulfate was 5.0 mg/m³.
Effect levels
open allclose all
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- 10.3 mg/m³ air
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- clinical signs
- food consumption and compound intake
- histopathology: non-neoplastic
- Key result
- Dose descriptor:
- NOEC
- Effect level:
- 5 mg/m³ air
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- clinical signs
- food consumption and compound intake
- histopathology: non-neoplastic
Target system / organ toxicity
- Key result
- Critical effects observed:
- not specified
Applicant's summary and conclusion
- Conclusions:
- The no-observed-adverse effect level (NOAEC) was 10.3 mg/m³, while the no-observed-effect level (NOEC) for exposure of rats to a dust aerosol of diammonium persulfate was 5.0 mg/m³. Furthermore, indications for respiratory tract irritation was observed in animals administered with 25 mg/m³ of diammonium persulfate.
- Executive summary:
The subchronic inhalation toxicity of ammonium persulfate was characterized using Sprague-Dawley rats (20/sex/group) at respirable dust concentrations of 0, 5.0, 10.3, and 25 mg/m³. Whole-body exposures were conducted 6 h/day, 5 days/week for 13 weeks. Gravimetric airborne test material samples were taken daily and particle size samples were taken weekly from each exposure chamber for analysis. Ten animals/sex/group were necropsied after 13 wk of exposure, and 5 animals/sex/group were held for 6- and 13-wk recovery periods. Animals were observed for clinical signs. Effects on body weight, food consumption clinical chemistry and haematology, ophthalmologic parameters organ weights, gross lesions, and histopathology were evaluated. There were no exposure-related deaths during the study. Increased respiration rates were noted in both males and females in the 25 mg/m³ group, and in a few animals in the 10.3 mg/m³ group. The incidence of these clinical signs decreased to zero during the first weeks of the recovery period. Body weights for both males and females in the 25 mg/m³ group were significantly depressed during most of the exposure period compared to the control group. By the end of the recovery period, body weights for the exposed animals were similar to the control group values. Lung weights were elevated in the 25 mg/m³ group after 13 wk of exposure, but were similar to controls at 6 wk postexposure. Irritation of the trachea and bronchi/bronchioles was noted microscopically after 13 weeks of exposure to 25 mg/m³. These lesions had recovered by 6 wk postexposure.
Based on these results, the no-observed-adverse-effect concentration (NOAEC) was 10.3 mg/m³, while the no-observed-effect concentration (NOEC) for exposure of rats to a dust aerosol of ammonium persulfate was 5.0 mg/m³.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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